blue whale

The blue whale, Balaenoptera musculus (Linnaeus 1758), is a widely
distributed species of baleen whale. Blue
whales in the Northern Hemisphere are generally smaller than those in the
Southern Ocean. Maximum body length in the North Atlantic was about 88.5
feet (27 m) and the largest blue whale reported from the North Pacific was
about 88 feet (26.8 m). Adults in the Antarctic can reach a maximum body
length of about 108 feet (33 m) and can weigh more than 330,000 pounds (150,000
kg).

As is true of other baleen whale species, female blue whales are somewhat
larger than males. Blue whales are identified by the following characteristics:
a long-body and comparatively slender shape; a broad, flat "rostrum" when
viewed from above; a proportionately smaller dorsal fin than other baleen
whales; and a mottled gray color pattern that appears light blue when seen
through the water.

Pygmy blue whale (B. m. brevicauda) – a significantly
smaller and morphologically distinct form found in the subantarctic
zone of the southern Indian Ocean and southwestern Pacific Ocean

Diet

The primary and preferred diet of blue whales is krill (euphausiids). In
the North Atlantic, blue whales feed on two main euphausiid species: ThysanoŽssa
inermis and Meganyctiphanes norvegica. In addition, T.
raschii and M. norvegica have been recorded as important food
sources of blue whales in the Gulf of St. Lawrence. In the North Pacific,
blue whales prey mainly on Euphausia pacifica and secondarily on T. spinifera. While other prey species, including fish and copepods,
have been mentioned in the scientific literature, these are not likely to
contribute significantly to the diet of blue whales.

Life
history

Scientists have yet to discern many details regarding the life history of
the blue whale. The best available science suggests the gestation period
is approximately 10–12 months and that blue whale calves are nursed
for about 6–7 months. Most reproductive activity, including births
and mating, takes place during the winter. Weaning probably occurs on, or
en route to, summer feeding areas. The average calving interval is probably
two to three years. The age of sexual maturity is thought to be 5–15
years. There are no known differences in the reproductive biology of blue
whales in the North Pacific and North Atlantic oceans.

Habitat

Blue whales inhabit sub-polar to sub-tropical latitudes. Poleward movements
in spring allow the whales to take advantage of high zooplankton production
in summer. Movement towards the subtropics in the fall allows blue whales
to reduce their energy expenditure while fasting, avoid ice entrapment in
some areas, and engage in reproductive activities in warmer waters of lower
latitudes. Although the species is often found in coastal waters, blue whales
are thought to occur generally more offshore than humpback whales, for example.

Distribution

Global

Blue whales are found in oceans worldwide and are separated into populations
by ocean basin in the North Atlantic, North Pacific, and Southern Hemisphere.
They follow a seasonal migration pattern between summering and wintering
areas, but some evidence suggests that individuals remain in certain areas
year-round. The extent of knowledge concerning distribution and movement
varies with area and migratory routes are not well known but, in general,
distribution is driven largely by food requirements. For example, in the
Gulf of St. Lawrence blue whales prefer deep waters where krill is concentrated.

North Atlantic

The overall distribution of blue whales in the North Atlantic extends from
the subtropics to Baffin Bay and the Greenland Sea. Blue whales are most
frequently sighted in the waters off eastern Canada, with the majority of
recent records from the Gulf of St. Lawrence, where they are present throughout
most of the year. They are most common during the summer and fall feeding
seasons and typically leave by early winter to avoid ice entrapment. Although
they are rare in the shelf waters of the eastern U.S., occasional sightings
of blue whales have been made off Cape Cod, Massachusetts. It is believed
this region may represent the current southern limit of the blue whales'
feeding range. In addition, there is some evidence to suggest that blue
whales occasionally stray into the Gulf of Mexico and the Caribbean, but
they are less common in these waters. Some scientists believe blue whales
in the North Atlantic occur in relatively discrete feeding populations whereas
other evidence suggests blue whales may comprise one "panmictic" population.

North Pacific

The blue whale's range is known to encompass much of the North Pacific Ocean,
from Kamchatka to southern Japan in the west, and from the Gulf of Alaska
and California south to at least Costa Rica in the east. The species is
found primarily south of the Aleutian Islands and the Bering Sea. Whaling
and sighting data suggest the existence of at least five subpopulations
of blue whales, with an unknown degree of mixing among them:

southern Japan (which appears to have been virtually "extirpated"
by whaling)

northern Japan/Kurils/Kamchatka

Aleutian Islands (the central stock, which may winter in deep water
north of Hawaii)

eastern Gulf of Alaska

California/Mexico

The International Whaling Commission (IWC), however, formally considers
only one management stock for blue whales in the North Pacific.

Northern Indian Ocean

There is a "resident" population of unknown taxonomic status present in
the northern Indian Ocean. Blue whales sightings have been reported from
the Gulf of Aden, Persian Gulf, Arabian Sea, and across the Bay of Bengal
to Burma and the Strait of Malacca. The migratory movements of these whales
are unknown.

Southern Hemisphere

In the Southern Hemisphere distributions of B. m. intermedia and B. m. brevicauda may be segregated. B. m. intermedia occurs mainly
in relatively high latitudes south of the "Antarctic Convergence" and close
to the ice edge. B. m. brevicada is typically distributed north
of the Antarctic Convergence.

Changes in distribution

There is some evidence which suggests the distribution and migratory patterns
of blue whales may have changed in at least four areas: northern Norway,
southern Japan, eastern Aleutian Islands, and northern California.

In northern Norway the paucity of sightings during recent surveys along
the coast where blue whales were common in the late 1800s and early 1900s,
may suggest that the historic distribution has changed. However, it could
also indicate depletion of the population by whaling.

In the western North Pacific, the lack of blue whales off southern Japan
today may also suggest that the distribution of these animals has changed
or that the animals of this region have been extirpated. South of the eastern
Aleutian Islands (160°W and 180°W), relatively large concentrations
of blue whales were documented in the 1970s but the species appears rare
there today, suggesting that illegal and unreported whaling depleted the
population.

Off northern California (e.g., Farallon Islands, Moss Landing, and Trinidad),
the recent appearance of numerous blue whales is noteworthy in light of
their rarity in these regions prior to the late 1970s. Such changes in distribution
may reflect a shift in feeding from the more offshore euphausiid, Euphausia
pacifica, to the primarily "neritic" euphausiid, ThysanoŽssa spinifera.

Population trends

Global

Blue whales were drastically depleted by commercial whaling activities worldwide,
in the 19th and first half of the 20th centuries. In the Southern Hemisphere,
pre-exploitation population estimates range from 150,000 to 210,000 whales;
recent abundance estimates range between 400 and 1,400 whales. In the North
Pacific, pre-exploitation population size is estimated as approximately
4,900 blue whales, whereas the current population estimate is a minimum
of 3,300 blue whales. In the North Atlantic, estimates for the entire basin
are considered unreliable, but range from 1,100 to 1,500 blue whales pre-exploitation,
and 100 to 555 whales currently.

Global abundance estimates for blue whales by ocean basin
(IWC, 2007)

Southern Hemisphere

North Pacific

North Atlantic

pre-exploitation

150,000–200,000

4,900

1,100–1,500

current

400–1,400

3,300

100–555

Western North Atlantic

Based on data from individuals found only in the Gulf of St. Lawrence, the
current minimum population estimate for the western North Atlantic stock
is 308 whales. It has estimated that the blue whale population in the western
North Atlantic during the late 1960s and early 1970s was in the very low
hundreds at most, and according to its most recent stock assessment, NMFS
has no evidence to refute this estimate. More than 320 individual blue whales
have been photo-identified in the Gulf of St. Lawrence and the total number
of photo-identified individuals for eastern Canada and New England is 352
as of Fall 1997.

According to the most recent NMFS stock assessment, there is insufficient
data to determine population trends for this species.

There are no accurate estimates of pre-exploitation population sizes available
for the western North Atlantic; however, several rough estimates have been
made by scientists. It has been approximated that there were more than 1,100
and as many as 1,500 blue whales in eastern Canadian waters.

Eastern North Atlantic

There is no current estimate for the number of blue whales in eastern North
Atlantic waters. However, some data have been collected for blue whales
in Icelandic waters. As of autumn 1997, 32 individuals had been photo-identified
in Icelandic waters. Additional studies have suggested that the population
in Icelandic and neighboring waters may be in the high hundreds or greater
than 1,000.

Sightings data off the west and southwest coasts of Iceland suggest the
population has been increasing at about five percent per year since the
late 1960s.

Despite these differences in pre-exploitation estimates and the lack of
estimates for current population abundance, it is clear that blue whale
stocks in the western, eastern, and central North Atlantic were severely
depleted by the time that legal protection was introduced in 1955.

Western North Pacific

There is insufficient data to evaluate the current abundance or population
trends of blue whale stocks in the western North Pacific, but blue whales
in Hawaiian waters are considered extremely rare.

Eastern
North Pacific

Blue whale abundance in the eastern Pacific is about 1,700. Along the California
coast blue whale abundance has been increasing during the past two decades.
The magnitude of this apparent increase is too large to be accounted for
by population growth alone and, therefore, it is assumed that a shift in
distribution has occurred. Although the population in the North Pacific
is expected to have grown since protection began in 1966, the possibility
of continued unauthorized takes, incidental ship strikes and mortality,
and serious injury in fishing gear makes this uncertain. Also, the evident
scarcity of blue whales in areas of former abundance (e.g., Gulf of Alaska
and near the Aleutian Islands) suggests that the increasing trend does not
apply to the species' entire range in the eastern North Pacific.

Threats

The primary threats currently facing blue whales are:

vessel strikes

fisheries interactions

Additional threats that have not been documented but could potentially affect
these populations include:

natural mortality

anthropogenic noise

competition for prey resources

habitat degradation

vessel disturbance

Although whaling substantially reduced blue whale populations worldwide
during the first half of the 20th century, whaling is no longer considered
a threat today.

Ship strikes

A primary threat to blue whales is mortality and serious injury caused by
ship strikes. In the eastern North Pacific, ship strikes were implicated
in the deaths of blues whales in 1980, 1986, 1987, 1993 and 2002. The average
number of blue whale mortalities in California attributed to ship strikes
was 0.2 per year from 1991–1995 and from 1998–2002. In September
2007, three blue whale mortalities were confirmed to be caused by ship strikes
in the Santa Barbara Channel off Southern California. These deaths were
part of a larger Unusual Mortality Event, declared by the Working Group
on Marine Mammal Unusual Mortality Events. In the western North Atlantic,
at least nine percent of the whales in the Gulf of St. Lawrence have injuries
or scars attributed to contact with ships. This area has a relatively high
risk of ship strikes because the St. Lawrence Seaway has heavy ship traffic
during the time of year when blue whales are relatively abundant. In March
1998, a dead 20 m (66ft) male blue whale was brought into Rhode Island waters
on the bow of a tanker. The cause of death was determined to be ship strike.
There are no records of ship strikes for blue whales in the western North
Pacific but mortalities caused by ship strikes have likely occurred without
being reported.

Fisheries interactions

Despite the lack of observed fisheries interactions in the last decade,
incidental take in fisheries threaten blue whales for two reasons. First,
past records of entanglements suggest that interaction with fishing gear
may affect blue whales. Second, entanglement rates may be underestimated
because blue whales may break through or carry away fishing gear, perhaps
suffering unrecorded subsequent mortalities or serious injuries. It is also
likely that stranding data underestimate the number of whales killed by
fishing gear, because most whales do not drift far enough to strand on beaches
or to be detected floating in the nearshore corridor. Although direct observation
of mortality is rare, at least two documented cases of dead blue whales
are apparently from the effects of entanglement in fishing gear (one in
1987 off Stellwagen Bank and the other in the 1990s in the Gulf of St. Lawrence).

Natural mortality

Little is known about natural mortality of blue whales in the North Atlantic.
Ice entrapment is known to injure and kill some blue whales, particularly
along the southwest coast of Newfoundland during late winter and early spring.
In the Gulf of St. Lawrence, scarring on the dorsal surface of some whales
is thought to be from contact with ice. Also, two blue whales bore rake-like
markings assumed to be from the teeth of killer whales (Orcinus orca).
However, no direct evidence of predation on blue whales has been reported
in this area.

A well-documented observation of killer whales attacking a blue whale off
Baja California proves that blue whales are at least occasionally vulnerable
to these predators. A high proportion of the blue whales in the Gulf of
California bear injuries or rake-like scars that are the result of encounters
with killer whales, although the extent to which such attacks are fatal
is unknown. Unlike in the western North Atlantic, injury or suffocation
from ice entrapment is not known to affect blue whales in the North Pacific.

Other potential non-primary threats

Anthropogenic noise, competition for prey resources, habitat degradation,
and vessel disturbance are additional concerns; however, there is little
evidence available to describe or quantify the impacts of these threats
on blue whales. For example, while anthropogenic noise is known to be a
threat for other cetaceans little is known about whether, or how, vessel
noise affects blue whales. Competition for prey resources is possible between
blue whales and other sympatric whale species but there is no direct evidence
for interspecific competition and it is unlikely blue whales compete with
humans for prey resources. Habitat degradation (e.g., chemical pollution)
has occurred in some areas of the North Atlantic (e.g., St. Lawrence River)
but the impacts of this degradation have not been proven to affect blue
whales and are understudied. Lastly, the effect of vessel disturbance (e.g.,
whalewatching boats) is of concern but there is no direct evidence to demonstrate
that persistent close approaches by tour boats has a negative effect on
blue whales.

Whaling

Blue whales were hunted as early as the 19th century but were not intensively
hunted until the turn of the 20th century. From the early 1900s to the mid-1960s
blue whales were hunted in all the world's oceans and their populations
significantly reduced. At least 9,500 blue whales were taken by commercial
whalers throughout the North Pacific between 1910 and 1965 and at least
11,000 were taken in the North Atlantic from the late 19th to mid 20th centuries.

In 1966, the IWC banned commercial whaling for blue whales and no whaling
(either "aboriginal subsistence" or commercial) occurs at present.

Illegal whaling for blue whales has been documented or is likely to have
occurred in the North Pacific, North Atlantic, and Southern Hemisphere.
A small number of illegal kills of blue whales have been documented in the
Northern Atlantic off Canada and Spain, and in the eastern North Atlantic.
Blue whales were also killed in the Southern Hemisphere by the Soviet Union
after 1966. Some illegal whaling by the USSR also occurred in the North
Pacific; it is likely that blue whales were among the species taken by these
operations, but the extent is not known.

No aboriginal whaling for blue whales is known to exist. Aboriginal hunters
who target whales off the coast of the Lesser Antilles and Greenland do
not target blue whales. Further, Norwegian whaling operations target only
minke whales, and the commercial whaling stations in Iceland, Spain, and
the Portugese islands of the Azores and Madeira remain officially closed.